Performance evaluation of rice–fish integration system in rainfed medium land ecosystem
Introduction
Indian agriculture, on supply side, has been subjected to tremendous pressure to provide food security due to stagnation in net cultivated area and increased population, which needs optimum utilization of land resources, in situ water conservation, multiple use of stored water and, finally, integrated farming practice to match the food demand in the coming years. Out of 42 million ha of rice cultivated land in India, about 20 million ha is suitable for adoption of rainfed rice–fish integration system (Rao and Ram Singh, 1998). However, only 0.23 million ha is presently under rice-fish culture (Mohanty and Mishra, 2003), where a productivity of 200–800 kg ha–1 offish has been obtained (Mukhopadhyay et al., 1991). Experience has proved the beneficial aspects of rice–fish integration system, which combines the principles of water conservation, soil improvement and biological control and plays an important role in sustainable production. Unfortunately, the carrying capacity of these suitable lands in India have not been utilized to the fullest extent. However, if these lands are brought under an integrated rice–fish system, it would help to compensate the economic losses in rice production brought about by natural calamities. This will also optimize the water and land use without bringing about environmental degradation. As paddy fields are complex ecosystems where primary producers and consumers at different levels compete with rice for material and energy, it decreases the overall productivity. However, fish culture in paddy fields can turn and recycle the available material and energy into fish production, accelerate the productivity of paddy fields and enhance the production potential of traditional farming practice (Caguan et al., 2000) with increased net income (Halwart, 1998).
Adoption and practice of rice–fish culture in India dates back almost 1500 years. The original system of integrated rice–fish farming, introduced to Southeast Asia from India, has flourished and developed from the low-input-based to intensive systems (Ali, 1990). However, despite great advances, several technical and production constraints are yet to be resolved such as yield gap between experimental and field models, inconvenience in pesticide application, and development of suitable design. It is also important to study the mechanism of rice–fish culture and the relationship among rice, fish and other factors such as soil, water, fertilization, etc. in the rice field. Although much works have been carried out on different aspects offish int egration system (Likangmin, 1988; Lightfoot et al., 1992; Huazhu, 1994; Fernando and Halwart, 2000; Kurup and Ranjeet, 2002), very little information are available on soil and water chemistry in relation to yield, impact of stocking density, design and management strategy to enhance unit yields. Keeping these in view, an attempt has been made to evaluate rice–fish integration system in rainfed medium land ecosystem with special reference to stocking density, growth performance of cultured species, system's rice equivalent yield and impact of weir height on system's overall performance.
Section snippets
Materials and methods
The present study was carried out at Deras Research Farm of WTCER, Bhubaneswar, India (Lat. 20°30’ N and Long. 87°48’10” E), during 1999-2001 for three successive years. Nine plots of 30 × 10 m size were selected for the proposed study. Three different weir heights (10, 12.5 and 15 cm) were maintained as treatment in triplicate along with peripheral trench of 0.5-m wide and 0.3-m deep. A slope of 0.5% was provided at the trench bottom towards the downstream side. Each plot was connected to adjacent
Results
The recorded minimum and maximum values of various water quality parameters during the experimental period were: water temperature, 27.5–30.2 °C; water pH, 6.9-8.8; dissolved oxygen, 3.9–8.1 ppm; total alkalinity, 49–119 ppm; transparency, 16-57 cm; dissolved organic matter, 0.6–4.7 ppm; nitrite-N, 0.006-0.071 ppm; nitrate-N, 0.06-0.52 ppm; ammonia, 0.01-0.31 ppm; total suspended solid, 89-319 ppm; phosphate-P, 0.06–0.34 ppm; water level/depth, 89-174 cm; and total plankton count, 2.4×102_9.1×103 nos/l.
Discussion
As rainfall and hydrograph of ponding in the rice fields are stochastic, substantial damage to crop and yield due to submergence or long dry spell at critical stages of crop growth takes place. This ultimately needs to determine the optimum weir/dyke height, so that there is maximum utilization of rainwater without any adverse effect on crop growth and yield. In our earlier experiment (Mishra et al., 1997), prior to this experiments, it was observed that deep percolation and seepage losses were
Acknowledgements
I warmly thank Dr. H.N. Verma, Director, WTCER (Indian Council of Agricultural Research), for providing me the necessary facilities for this experiment and Dr. S.K. Mohanty, Fisheries Consultant, Chilika Development Authority, Orissa, India, for reviewing the manuscript.
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